MINING FOR CLOSURE
15
Sweden, and the United States and that this trend
will undoubtedly continue.
26
Present-day attitudes to environmental protection
are increasingly represented in the development of
the concept of sustainable development, of “triple
bottom line accounting”, of cleaner production, of
life-cycle assessment to assess potential impacts, of
the precautionary principle, and of environmental
impact assessment to advise decision-makers and
the broader community on the potential negative as
well as positive outcomes of a proposed development.
All of these are relevant o the mining industry, and
extend from the pre-mine planning phase, through
construction, mining, and mine closure to post-mine
stewardship (Environment Australia, 2002b).
According to Sassoon (2000), integrated mine
planning – a term intended to capture the general
ethos of
“Mining for Closure”
means that to achieve
this:
... a mine closure plan should be an integral part of
a project life cycle and be designed to ensure that:
Future public health and safety are not com-
promised;
27
Environmental resources are not subject to
physical and chemical deterioration;
28
The after-use of the site is beneficial and sus-
tainable in the long term;
Any adverse socio-economic impacts are min-
imised; and
All socio-economic benefits are maximised.
and in Australia key minerals industry representa-
tive groups
29
hold that:
Mine rehabilitation is an ongoing programme
designed to restore the physical, chemical and bio-
logical quality or potential of air, land and water
regimes disturbed by mining to a state acceptable
to the regulators and to post-mining land users.
The objective of mine closure is to prevent or mini-
mise adverse long-term environmental impacts,
and to create a self-sustaining natural ecosystem
or alternate land use based on an agreed set of ob-
jectives (ANZMEC MCA, 2000, p. v)
30
However, it is clear from such instances as the 1985
Stava tailings dam failure in Trento, Italy where 268
people were killed, the tailings dam collapse at Los
Frailes in Spain in April 1998 and the Baia Mare
cyanide spill in Romania in January 2000,
31
that
mining activities still pose risks of significant en-
vironmental, social and economic harm. There is a
significant need for improvements in the standard
of the environmental protection policies, manage-
ment systems and technologies applied at many
mine sites. In many settings, it is the removal of
present and significant risk (and danger) that must
have an immediate and pressing priority. In seek-
ing to ameliorate or remove such risks however, the
broader objectives of longer term sustainability –
and
Mining for Closure
– as shall be discussed in this
26. In this instance, the author is principally referring to legislative
requirements for financial assurance for closure and reclamation.
27. Generally as posed by safety hazards such as unstable tailings
impoundments, toxic waters, unsafe buildings, equipment, open
holes, and so forth. However, it must be recognised that few (if
any) items in the built or natural environment are “hazard free”.
Thus, it is reasonable to expect that assume that in all countries
there should be transparent debate and agreement on the level
of acceptable risk pertinent environmental, social and economic
aspects of mines and mining facilities post-closure. Further, the
reader is referred to definitions of risk and hazard provided in the
glossary of terms for this document.
28. The terms applied here, as drawn fromEnvironmental Aspects
of Mine Closure produced by Sassoon (2000) and Mining for the
Future: Appendix B - Mine Closure Working Paper produced by
van Zyl, Sassoon, Fleury & Kyeyune (2002a) are generic but are
intended to bear with them the intent and limitations presented
in the source documents. Clearly the requirements for physical
and chemical stability of physical resources and achievement of
land use categories are not without bound. The reader is referred
to the source documents for such.
29. Australian and New Zealand Minerals and Energy Council
(ANZMEC) and the Australian Minerals Industry (represented by
the Minerals Council of Australia (MCA).
30. Note however, that the broadness of these positions are not
universally shared as the following comment from a South Afri-
can mining company representative demonstrates:
“From the min-
ing company’s point of view, the principal actions and liabilities associ-
ated with mine closure at present are: the retrenchment of employees
and the cost of associated severance packages as well as in some cases
mitigatory funds for the retraining of retrenched employees; the reha-
bilitation of the areas disturbed by mining and associated activities in
line with statutory obligations”
(Reichardt, 2002p, 2B-1).
31. To quote the European Commision (European Commission,
2003):
The collapse of heaps and dams can have a serious impact on
the environment and on human health and safety. The collapse of a
heap of inert waste from a coal mine at Aberfan in Wales in 1966 was
the worst ever such accident in the UK and caused the deaths of 144
people, mainly children. As for tailings dams, at world level these have
failed at an average of 1.7 per year over the past 30 years. At Stava,
Italy, in 1985, a fluorite tailings dam failed and released 200,000 m³ of
inert tailings, killing 268 people and destroying 62 buildings. At Aznal-
cóllar, Spain, in 1998, an accident in an area close to the Doñana
Natural Park in South Andalusia released into the River Guadiamar
2 million m³ of tailings and 4 million m³ of water contaminated by
heavy metals. At Baia Mare in Romania in 2000 a tailings pond burst
releasing approximately 100,000 m³ of waste water containing up to
120 tonnes of cyanide and heavy metals into the River Lapus; this then
travelled downstream into the Rivers Somes and Tisa into Hungary
before entering the Danube. In Baia Borsa, also in Romania, 20,000
tonnes of tailings were released into the River Novat, a tributary of the
Rivers Viseu and Tisa.
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